United States [Environmental Protection Agency Atmospheric Research and Exposure Assessment Laboratory Research Triangle Park NC 27711 Research and Development EPA/600/S3-90/005 Mar. 1990 &EPA Project Summary Development and Validation of a Test Method for Formaldehyde Emissions E. D. Estes, W. F. Gutknecht, D. L Hardison, G. B. Howe, R. K. M. Jayanty, and J. A. O'Rourke Formaldehyde has been identified as a suspect carcinogen and may be regulated in the future as a hazardous air pollutant under Section 112 of the Clean Air Act. The full report details the field validation of a test method for sampling and analyzing formaldehyde emissions from stationary sources. Three potential source methods were evaluated. One method, the basic peroxide impinger/ion chroma- tography (1C) method is based upon the dissolution and oxidation of formaldehyde in the impinger reagent to form formate ion, which is measured by 1C. The second method is a dinitrophenylhydrazine-coated (DNPH) cartridge/high performance liquid chromatography (HPLC) method, which is based on the reaction of formaldehyde with 2,4- DNPH and subsequent analysis of the hydrazone derivative by HPLC. The third method, the DNPH irnpinger/HPLC method extends the range of the cartridge method through the use of higher capacity DNPH impinger solutions. Field testing of the methods were conducted at two different sites. At a formaldehyde manufacturing plant, where formaldehyde levels were high (> 100 mg/cu m), samples were collected using the basic peroxide impinger method and the DNPH impinger method. At a formaldehyde user facility, where formaldehyde levels were low, samples were collected using the DNPH-coated cartridge method and the DNPH impinger method. A statistical evaluation indicates that the DNPH impinger method is acceptable for determining both low and high concentrations of formaldehyde. Because of its range, this method is recommended as the reference method for determination of formaldehyde in source emissions. The full report is submitted in fulfillment of EPA Contract Nos. 68- 02-4125 and 68-02-4550 by the Research Triangle Institute under the sponsorship of the U.S. Environmental Protection Agency. The report covers a period from February 1987, through April 1989. This Project Summary was developed by EPA's Atmospheric Research and Exposure Assessment Laboratory, Research Triangle Park, NC, to announce key findings of the research project that is fully documented in a separate report of the same title (see Project Report ordering information at back). Introduction Formaldehyde has been identified as a suspect carcinogen and may be regulated in the future as a hazardous air pollutant under Section 112 of the Clean Air Act. The U. S. Environmental Protection Agency (USEPA) has an ongoing program to evaluate and ------- Methods Evaluated smaller 9as was manufactunng se a^iST', ,3' the were made a, each ste1ThePd"ferent da^s minutes in r"nS Were 45 SrSofofzwedaala-'h- ^oX^^-rinT"- solution/high (HPLC> imP'n9er .T-.-^MC uenvative by HPI P Th« Sample Analysis wc resulted n inc easd formaldehyde concpnt«f- operations were S« H"; Statistical the DNPH . C°mpare rr s~;^e;rcs • - -p—n,, rmamln'9 'Cant breaktnrough FoMhl ~mpa™on of the me, th'r,m 9 'mpm9er pairs. *e contents of °' vanance for a two " aTn^:5:^™^^a"d"u.ed the 1 9 ana|ysis classification Sample Collection equipped w a o Varian UV-50 detector set at 365 HPLC °op and a . The DNPH gravity ,eed us,ng 6 eluate was collectprt , 'lasks and dH^d h Measurements we re mil mark HPLC system descnbed^bte'3'"9 th Preparation ™pinger prior to DNPH ------- increased. The average BSD for these data was 1.9 percent with a range of 0.9 to 3.9 percent. The respective, pooled standard deviations for the impinger and cartridge data were calculated to be 4.9 and 2.1 percent. A comparison of the means again using analysis of variance indicated the methods to be significantly different at the 95 percent confidence level. The average difference was calculated to be 0.079 mg/cu m or 7.5 percent, with the DNPH cartridges producing demonstrably higher values. Several parameters which collectively may have contributed to this difference include slightly lower collection efficiency in the impingers, loss from the impingers (in the form of aerosol), and some minor interferent or formaldehyde background on the cartridges. The average recovery for the DNPH-formaldehyde derivative spike at the user site was 92 percent, which supports the first of the two possible reasons given for the difference between the methods. Conclusion The best precision was obtained with the DNPH-coated cartridge/HPLC method, which had a pooled standard deviation of 0.023 mg/cu m. The method was also the easiest to use, with no possibility of sample containers breaking or reagents spilling in the field. However, the capacity of the cartridge was exceeded quickly at the high concentrations (> 100 mg/cu m) of formaldehyde generally present at the formaldehyde manufacturing facilities. The DNPH impinger/HPLC method was tested at both the formaldehyde manufacturing site and the formaldehyde user site. A statistical evaluation indicates that this method is acceptable for determining both low and high concentration levels of formaldehyde. Because of its poor detection limit, the basic peroxide impinger/IC method was found to b e unsuitable for the determination of very low levels of formaldehyde (0.5 to 5 mg/cu m) such as those found at formaldehyde user sites. The method also yielded unacceptable results for the very high concentrations of formaldehyde (> 500 mg/cu m) sometimes found at formaldehyde manufacturing facilities, because the formaldehyde is not completely oxidized to formate ion. The method does show potential at intermediate levels (50-300 mg/cu m), and, because the reagents used are safer and easier to prepare in the field than those used for the DNPH impinger method, it is recommended that the oxidation reaction be studied further. The major objective of the study was to develop and recommend a single method for sampling and analysis of formaldehyde over a wide range of concentrations (< 1 mg/cu m to > 500 mg/cu m). The DNPH impinger/HPLC method meets this requirement and is therefore recommended as the reference method. However, in view of the excellent precision obtained for the DNPH-coated cartridge method and its ease of use, it is recommended that this method be approved as an alternate when low levels of formaldehyde are expected. ------- E. D. Estes, W. F. Gutknecht, D. L. Hardison, G. B. Howe, R. K. M. Jayanty and J. A. O'Rourke are with Research Triangle Institute, Research Triangle Park, NC 27709. Jimmy C. Pau is the EPA Project Officer (see below). The complete report, entitled "Development and Validation of a Test Method for Formaldehyde Emissions," (Order No. PB-90-183-419AS; Cost: $17.00 subject to change) will be available only from: National Technical Information Service 5285 Port Royal Road Springfield, VA22161 Telephone: 703-487-4650 The EPA Project Officer can be contacted at: Atmospheric Research and Exposure Assessment Laboratory U.S. Environmental Protection Agency Research Triangle Park, NC 27711 United States Center for Environmental Research Environmental Protection Information Agency Cincinnati OH 45268 Official Business Penalty for Private Use $300 EPA/600/S3-90/005 ------- |